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ARCHIVED REPORTS_XR0004270
Environmental Health - Public
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PR0541913
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ARCHIVED REPORTS_XR0004270
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Last modified
2/13/2020 5:16:35 PM
Creation date
2/13/2020 1:37:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004270
RECORD_ID
PR0541913
PE
2960
FACILITY_ID
FA0024043
FACILITY_NAME
FRONTIER TRANSPORTATION FACILITY
STREET_NUMBER
425
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220009
CURRENT_STATUS
01
SITE_LOCATION
425 LARCH RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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�y. Quarterly Groundwater Report <br /> iFrontier Transportation <br /> ' 0801-052 <br /> August 27, 2001 <br /> Page 4 <br /> ' No detectable concentrations of dissolved BTEX were identified in groundwater samples <br /> collected in August 2001 from monitoring wells MW-1, MW-2, MW-4, MW-5, MW-6, MW-7, <br /> ' MW-8, MW-9, MW-10, and MW-11 using EPA method 8020. Monitoring well MW-3 <br /> exclusively identified total dissolved BTEX at a concentration of 1,889 pg/L, an increase from <br /> 230 pg/L identified in April 2001. The potentiometric level dropped by 0.28' in well MW-3, <br /> which may have dissolved adsorbed BTEX still present in the soil. Total dissolved BTEX <br /> concentrations in MW-3, however, have attenuated by 77% since the maximum was identified as <br /> 8,350 }ig/L in March 1998 when groundwater rose to its shallowest depth recorded (7.l' bg). <br /> See Figure 5 for the recent dissolved BTEX Isoconcentration Map. <br /> MTBE was identified in groundwater from one monitoring well (MW-3) only in August <br /> ' 2001. Groundwater collected from monitoring well MW-3 identified an increase in MTBE <br /> concentrations from 250 pg/L to 1,300 pg/L, since the previous monitoring episode (April 2001) <br /> using EPA method 8260. The potentiometric level in MW-3 dropped 0.28' between the two <br /> ' groundwater monitoring episodes. The drop in the groundwater level may have dissolved <br /> adsorbed MTBE in the soil. However, MTBE concentrations have attenuated by 96% from the <br /> maximum concentration of 29,400 µg/L identified in MW-3 during March 1998. No detectable <br /> concentrations of oxygenates were identified from groundwater sample analysis of the remaining <br /> all ten monitoring wells using EPA method 8260 (See Appendix B). See Figure 6 for the recent <br /> MTBE Isoconcentration Map. <br />' 5.0) CONCLUSIONS AND RECOMMENDATIONS <br />' Based on groundwater sample analysis results, the dissolved TPH-d, TPH-g, TPH-m, <br /> BTEX, and MTBE plumes are spatially stable on-site and confined to the former UST location. <br /> No detectable concentrations of dissolved TPH-d, TPH-g, TPH-m, BTEX, and MTBE were <br />' identified in ten of the total eleven monitoring wells dedicated to the site. Dissolved TPH-g, <br /> BTEX, and MTBE were identified in monitoring well MW-3 exclusively located just east of <br />' former UST location. Attenuation of the above petroleum hydrocarbons has been identified in <br /> MW-3 since their respective recorded maximums identified in March 1998. <br /> BEII recommends that quarterly groundwater monitoring continue at the site until <br /> constant or decreasing dissolved petroleum hydrocarbon concentrations are observed. <br /> Groundwater samples will be analyzed for BTEX using EPA method 8020, TPH-d and TPH-g <br />' using EPA method 8015m, and oxygenates using EPA method 8260 in all future monitoring <br /> episodes as directed by the PHS/EHD. In addition, BEII requests that groundwater analysis for <br /> TPH-m will no longer be performed at the site. <br /> i <br />
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